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EC number: - | CAS number: -
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Partition coefficient
Administrative data
Link to relevant study record(s)
- Endpoint:
- partition coefficient
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 18-07-2013 to 05-09-2013
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Remarks:
- Guideline study performed under GLP. All relevant validity criteria were met.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 123 (Partition Coefficient (1-Octanol / Water), Slow-Stirring Method)
- Deviations:
- no
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- EU Method A.23 Partition Coefficient (1-Octanol/Water): Slow-Stirring Method
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- inspected: July 2012 ; signature: November 2012
- Type of method:
- slow-stirring method
- Partition coefficient type:
- octanol-water
- Specific details on test material used for the study:
- - Physical state: Liquid
- Storage condition of test material: Approximately 4°C in the dark under nitrogen
- Other: clear colourless liquid - Analytical method:
- gas chromatography
- Type:
- log Pow
- Partition coefficient:
- >= 4.23 - <= 4.29
- Temp.:
- 25 °C
- pH:
- 6.4
- Remarks on result:
- other: basis of two (n=2) constituent peaks with peak area > 10%
- Conclusions:
- The octanol / water partition coefficient was determined to be log Pow = 4.23 to 4.29 at 25 ± 0.5 °C and pH 6.4.
- Executive summary:
The octanol / water partition coefficient was determined to be log Pow = 4.23 to 4.29 at 25 ± 0.5 °C and pH 6.4. The partition coefficient of the substance was determined according to OECD TG 123 slow stirring method under GLP, at 25 ± 0.5 °C from three independent replicates (test vessels) with four utilised out of seven sub-replicates (samples). Three sub-replicates were excluded due to problems with sample treatment and not utilised in further calculations. The pH-value of the aqueous phases was determined by a pH-meter. The pH of the aqueous phase at t=147 hours equilibration (before) was pH: 7.1 to 7.3 in all replicates and at t=478 hours equilibration (after) was pH: 6.4 – 6.5. Analytical evaluation was performed using GC-FID on a capillary analytical column using an internal calibration reference substance. The analytical method was validated. The linearity of the detector response with respect to concentration was assessed for aqueous and organic phases respectively, and satisfactory correlation coefficient (r2) of 1.000 obtained. Mean log Pow values in the equilibration time for each replicate fell within a range of ± 0.3 log for the two main constituent isomers. equilibrium was evident from 214 hours equilibration time. Taking the results for samples 3, 4, 5 and 7 for each vessel, the slope of the correlation was tested statistically to ensure it did not differ significantly from zero. This was performed using the t test and a probability value of P = 0.05 (critical value = 4.30 for 2 degrees of freedom). A slope not significantly different from zero of at least 4 points verified the attainment of equilibrium. The octanol / water partition coefficient was determined to be log Pow = 4.23 to 4.29 at 25 ± 0.5 °C and pH 6.4..
Reference
Description of key information
log Pow (slow stir) = 4.23 to 4.29 at 25 ± 0.5 °C and pH 6.4, OECD TG 123, 2014
Key value for chemical safety assessment
- Log Kow (Log Pow):
- 4.29
- at the temperature of:
- 25 °C
Additional information
Key study : OECD TG 123, 2014 : The octanol / water partition coefficient was determined to be log Pow = 4.23 to 4.29 at 25 ± 0.5 °C and pH 6.4. The partition coefficient of the substance was determined according to OECD TG 123 slow stirring method under GLP, at 25 ± 0.5 °C from three independent replicates (test vessels) with four utilised out of seven sub-replicates (samples). Three sub-replicates were excluded due to problems with sample treatment and not utilised in further calculations. The pH-value of the aqueous phases was determined by a pH-meter. The pH of the aqueous phase at t=147 hours equilibration (before) was pH: 7.1 to 7.3 in all replicates and at t=478 hours equilibration (after) was pH: 6.4 – 6.5. Analytical evaluation was performed using GC-FID on a capillary analytical column using an internal calibration reference substance. The analytical method was validated. The linearity of the detector response with respect to concentration was assessed for aqueous and organic phases respectively, and satisfactory correlation coefficient (r2) of 1.000 obtained. Mean log Pow values in the equilibration time for each replicate fell within a range of ± 0.3 log for the two main constituent isomers. equilibrium was evident from 214 hours equilibration time. Taking the results for samples 3, 4, 5 and 7 for each vessel, the slope of the correlation was tested statistically to ensure it did not differ significantly from zero. This was performed using the t test and a probability value of P = 0.05 (critical value = 4.30 for 2 degrees of freedom). A slope not significantly different from zero of at least 4 points verified the attainment of equilibrium. The octanol / water partition coefficient was determined to be log Pow = 4.23 to 4.29 at 25 ± 0.5 °C and pH 6.4.
Applicant assessment indicates: the log Pow of each chromatographic constituent peak > 1% was determined within the study. The two main peaks (peak area > 10%) are reported as the substance log Pow range: 4.23 to 4.29 at 25 ± 0.5 °C and pH 6.4. All other peaks < 10% peak area had : log Pow 3.63 to 4.04. These are excluded from further consideration. The two main chromatographic peaks are considered to be the main constituent isomers and/or are most relevant for Classification and Labelling and Environmental Risk Assessment.
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